Environmental Screening Of

Total Page:16

File Type:pdf, Size:1020Kb

Environmental Screening Of Coachella Valley Stormwater Channel Improvement Project, Avenue 54 to Thermal Drop Structure Draft Environmental Impact Report / State Clearinghouse No. 2015111067 Appendices APPENDIX C Coachella Valley Stormwater Channel Improvement Project, Phase I Biological Resources Assessment & Coachella Valley Multiple Species Habitat Conservation Plan Compliance Report City of Coachella and Unincorporated Community of Thermal Submitted to: Terra Nova Planning & Research, Inc. 42635 Melanie Place, Suite 101 Palm Desert, CA 92211 Submitted by: Amec Foster Wheeler, Environment & Infrastructure, Inc. 3120 Chicago Avenue, Suite 110 Riverside, CA 92507 3 February 2016 Coachella Valley Water District C-1 Coachella Valley Stormwater Channel Improvement Project, Phase I Biological Resources Assessment & Coachella Valley Multiple Species Habitat Conservation Plan Compliance Report City of Coachella and Unincorporated Community of Thermal Riverside County, California Submitted to: Terra Nova Planning and Research, Inc. 42635 Melanie Place, Suite 101 Palm Desert, CA 92211 Contact: John Criste (760) 341-4800 [email protected] Submitted by: Amec Foster Wheeler, Environment & Infrastructure, Inc. 3120 Chicago Avenue, Suite 110 Riverside, CA 92507 Contact: John F. Green Senior Biologist (951) 369-8060 [email protected] 3 February 2016 Coachella Valley Stormwater Channel Improvement Project, Phase I Biological Resources Assessment & MSHCP Compliance Report February 2016 EXECUTIVE SUMMARY For the purposes of this assessment, analysis of the proposed Coachella Valley Stormwater Channel (CVSC) Improvement Project, Phase I (project) could include the following: Extension of existing and construction of new concrete-lined channel/levee banks, a fully concrete-lined channel from Airport Boulevard to the Thermal Drop Structure near Avenue 58, and construction of a bypass channel or combinations thereto. Modification of the existing channel cross-section and Thermal Drop Structure. Improvement of the levees (construct above-grade concrete barriers) upstream of Airport Boulevard to the vicinity of Avenue 54. Future modification to the northernmost railroad bridge may be required. The project is located both within the city limits of Coachella and unincorporated lands in the community of Thermal, Riverside County, California. The approximately 262 acre Project Planning Area/Area of Potential Effect (PPA/APE) is approximately two miles long in and adjacent to the CVSC. The PPE/APE extends from immediately north of Avenue 54 downstream (south) to north of Avenue 58 in Thermal. The existing CVSC is bounded by earthen flood control levees, although concrete wall reinforcement is present in the northern PPA/APE and near bridges. Land outside the CVSC, but in and surrounding the PPA/APE is a patchwork of commercial buildings and single-family rural residential dwellings, agriculture, and natural lands (undeveloped, some of which have been previously disturbed). Information contained herein is intended to be used for compliance with state and federal regulations intended to protect waters and special status species and their habitats. This includes the Coachella Valley Multiple Species Habitat Conservation Plan (CVMSHCP), the boundaries of which the PPA/APE is within. In preparation for the field visits, a literature review was conducted to identify special-status biological resources known from the vicinity of the PPA/APE. The literature review included the following documents: California Natural Diversity Data Base (CNDDB) RareFind 5 California Native Plant Society's Inventory of Rare, Threatened, and Endangered Plants of California The CVMSHCP documents United States Department of Agriculture, Natural Resources Conservation Service, Web Soil Survey United States Geological Survey 7.5’ Indio, Mecca, Valerie, and Thermal Canyon, Calif. quadrangles Two field assessment visits were conducted, including a focused burrow survey for burrowing owls. PPA/APE suitable habitat was assessed based on the presence or absence of habitat components (e.g., soils, vegetation and topography) characteristic of the potentially occurring special-status biological resources determined by the literature review. Pedestrian transects were walked over the entire PPA/APE where accessible. All flora and fauna observed or otherwise detected (e.g., dead remains [primarily plants], vocalizations, presence of scat, tracks, i Coachella Valley Stormwater Channel Improvement Project, Phase I Biological Resources Assessment & MSHCP Compliance Report February 2016 and/or bones) during the course of this assessment were recorded in field notes and included in Appendices 1 and 2. Topography, soils, and vegetation (natural communities) were mapped. The literature review and biological resources assessment resulted in the identification of 50 special-status species which were observed in the PPA/APE, had CNDDB records within an approximate five mile radius of the PPA/APE, and/or which had habitat, including CVMSHCP modeled habitat, in the PPA/APE. These included 14 plants, two invertebrates, two fishes, one amphibian, two reptiles, 22 birds, and seven mammals. Of the 50 sensitive elements identified by the literature review to occur in the PPA/APE vicinity (see Tables 2-8 above), 18 were determined to be absent from the PPA/APE, including all of the plant species, the cheeseweed owlfly, the razorback sucker, Coachella Valley fringe-toed lizard, and the Colorado Valley woodrat. Since they are not expected to occur within the PPA/APE or be impacted, those 18 species will not be discussed further. Of the remaining 32 species, seven are fully covered and conserved by the CVMSHCP: desert pupfish, flat-tailed horned lizard, southwestern willow flycatcher, least Bell’s vireo, western yellow bat, Palm Springs pocket mouse, and Coachella Valley (Palm Springs) round-tailed ground squirrel. Since potential impacts to these seven species will be mitigated through project participation in the CVMSHCP as a covered activity, they will not be discussed further. The monarch, a butterfly, is not covered by the CVMSHCP. It is ranked S2S3 by the state (imperiled - vulnerable), but has no other state or federal status. The species is considered special-status primarily because of its wintering roosts along the coast. A single butterfly was seen foraging in the PPA/APE. We are not recommending any further action in regard to this species, as the PPA/APE is not coastal and does not contain any known monarch roost sites The Couch’s spadefoot is not covered by the CVMSHCP. It is considered a species of special concern by the California Department of Fish and Wildlife (CDFW) and is ranked S2 by the state (imperiled), but has no other state or federal status. It may occur in temporary rain pools, and flooded date palm orchards may also provide breeding habitat and refugia. There is only one known local record, five miles to the southeast, and limited potential habitat in the PPA/APE. Amec Foster Wheeler recommends that substantial temporary pools and orchards be avoided or surveyed for this species and its’ larvae prior to disturbance to avoid impacts to breeding spadefoots. This does not include the channel itself. Three additional species of bats were found to have records in the PPA/APE vicinity: Townsend’s big-eared bat, spotted bat, and western mastiff bat. One of these, the spotted bat, only has foraging potential in the PPA/APE. Although implementation of the proposed project may represent an incremental loss of potential spotted bat foraging habitat, it is not expected to have a significant impact on the species or to result in its take. We are not recommending any further action on behalf of the spotted bat. The Townsend’s big-eared bat could roost on the walls and ceilings of bridges, culverts, and other structures in the PPA/APE, but is most often associated with caves or mines. Human disturbance is frequent in the PPA/APE, and may be a limiting factor for this species. The western mastiff bat prefers roosts in high places such as cliff crevices, but could use trees or structures in the PPA/APE. Both species may forage in the PPA/APE. Take of these or other roosting bat species may be considered significant. Although no bats were seen during the biological resource assessment, suitable roosting habitat was seen. ii Coachella Valley Stormwater Channel Improvement Project, Phase I Biological Resources Assessment & MSHCP Compliance Report February 2016 Focused surveys may be required to ensure that bats are not present so that they are not harmed or disturbed by construction activities. The California black rail and Yuma Ridgway’s (clapper) rail are covered species under the CVMSHCP, but because they are both California Fully Protected species, no take is allowed. Also, because the California black rail is not federally listed, take of that species is also prohibited under the Migratory Bird Treaty Act (MBTA). For both species, the CVMSHCP states: “Surveys will be required in potential Habitat for this rail before any activity that would impact the Habitat. If rails are found, the Habitat must be avoided or measures approved by The Wildlife Agencies taken to ensure that no take of an individual occurs.” Potential habitat is present in the CVSC and these species have been recorded in the area. Surveys for these species are conducted between March 15th and May 31st. If either species was found to be present, consultation with the wildlife agencies would be required prior to any impacts to habitat.
Recommended publications
  • Chapter 10 Open Channels
    Chapter 10 Open Channels Chapter 10 Open Channels Table of Contents 10-1 Introduction ...................................................................................................................................... 1 10-1-1 Chapter Overview ............................................................................................................. 1 10-1-2 Design Flows .................................................................................................................... 1 10-1-3 Channel Types .................................................................................................................. 2 10-1-4 Sediment Loads ................................................................................................................ 5 10-1-5 Permitting and Regulations ............................................................................................... 6 10-2 Natural Stream Corridors ............................................................................................................... 7 10-2-1 Functions and Benefits of Natural Streams ...................................................................... 8 10-2-2 Effects of Urbanization ..................................................................................................... 9 10-2-3 Preserving Natural Stream Corridors .............................................................................. 11 10-3 Stream Restoration Principles .....................................................................................................
    [Show full text]
  • Drainage and Erosion Control Design Manual
    City of West Lake Hills Drainage and Erosion Control Design Manual May 2020 TABLE OF CONTENTS Chapter 1 Introduction ....................................................................................................... 1 1.1 Purpose and Scope ....................................................................................................... 1 1.2 Applicability .................................................................................................................... 1 1.3 Waivers ............................................................................................................................ 1 1.4 Amending the Manual .................................................................................................. 1 1.5 References and Definition of Terms ............................................................................ 1 Chapter 2 Drainage Criteria .............................................................................................. 3 2.1 Permit Submittal Components ..................................................................................... 3 2.1.1 Preliminary Drainage Plan ......................................................................................... 3 2.1.2 Type I Development Submittal ................................................................................. 4 2.1.3 Type II Development Submittal ................................................................................ 4 2.1.4 Type III Development Submittal ..............................................................................
    [Show full text]
  • CHAPTER-6 Cross-Drainage and Drop Structures 6.1 Aqueducts and Canal Inlets and Outlets 6.1.1 Introduction
    Cross-Drainage and Drop Structures CHAPTER-6 Cross-Drainage and Drop Structures 6.1 Aqueducts and canal inlets and outlets 6.1.1 Introduction The alignment of a canal invariably meets a number of natural streams (drains) and other structures such as roads and railways, and may sometimes have to cross valleys. Cross drainage works are the structures which make such crossings possible. They are generally very costly, and should be avoided if possible by changing the canal alignment and/or by diverting the drains. 6.1.2 Aqueducts An aqueduct is a cross-drainage structure constructed where the drainage flood level is below the bed of the canal. Small drains may be taken under the canal and banks by a concrete or masonry barrel (culvert), whereas in the case of stream crossings it may be economical to flume the canal over the stream (e.g. using a concrete trough, Fig. 6.1(a)). When both canal and drain meet more or less at the same level the drain may be passed through an inverted siphon aqueduct (Fig. 6.1(d)) underneath the canal; the flow through the aqueduct here is always under pressure. If the drainage discharge is heavily silt laden a silt ejector should be provided at the upstream end of the siphon aqueduct; a trash rack is also essential if the stream carries floating debris which may otherwise choke the entrance to the aqueduct. 6.1.3 Superpassage In this type of cross-drainage work, the natural drain runs above the canal, the canal under the drain always having a free surface flow.
    [Show full text]
  • Lower Long Tom River Haibtat Improvement Project
    Lower Long Tom River Habitat Improvement Plan 2018 Developed by: Confluence Consulting, LLC and Long Tom Watershed Council Lower Long Tom River Habitat Improvement Plan January 2018 1 | P a g e Table of Contents Executive Summary ............................................................................................................................................................................... 4 Introduction............................................................................................................................................................................................ 6 Study Goals and Opportunities ...................................................................................................................................................... 7 Stakeholders and Contributors ....................................................................................................................................................... 7 Background on the Lower Long Tom River .................................................................................................................................... 9 Long Tom Fisheries ............................................................................................................................................................................ 11 Fishery Background (excerpted from the US Army Corps of Engineers report “Long Term on the Long Tom,” February 2014) ...............................................................................................................................................................................
    [Show full text]
  • 1 Isaac River Condition, Condition Trajectory and Management
    Memo Subject Response to information request from DEHP From Rohan Lucas Distribution BMA Date 12 February 2016 Project Broadmeadow EA amendment – Watercourse Subsidence 1 Isaac River condition, condition trajectory and management 1.1 Request The administering authority requires more information relating to the proactive management strategies that BMA will adopt to ensure the condition trajectory of the diversion is not negatively impacted by subsidence. 1.2 Response Understanding the incremental risk posed by subsidence The Isaac River diversion, constructed in the mid 1980’s was undertaken to a different standard to that which would be adopted today. The diversion underwent major erosional adjustment in the 1980’s and 1990’s (see Figure 2). Following some management intervention in the mid-late 1990’s (including timber pile fields) and a period without any major flow events from 1991 to 2007 (refer to Figure 1), the diversion underwent substantial recovery. This recovery included the deposition of benches against toe of bank and colonisation of those benches with riparian vegetation, providing a near continuous coverage along the diversion. These vegetated benches protect the near vertical, erodible upper banks from erosion in the majority of flow events (refer Figure 3). The diversion, which reduced river length by several kilometres, was constructed with two drop structures to compensate for the increase in gradient. One of these structures is now largely redundant and the other has been subject to damage from flow events and repair on numerous occasions. The remaining functional structure performs its design intent during smaller flows but is ineffective in larger flows in reducing energy conditions sufficiently.
    [Show full text]
  • SEEDS) Sustainability Program Student Research Report
    UBC Social Ecological Economic Development Studies (SEEDS) Sustainability Program Student Research Report Replacement of the Spiral Drain at the North End of UBC Campus Mona Dahir, Jas Gill, Danny Hsieh, Rachel Jackson, Michael Louws, Chris Vibe University of British Columbia CIVL 446 April 7th, 2017 Disclaimer: “UBC SEEDS Sustainability Program provides students with the opportunity to share the findings of their studies, as well as their opinions, conclusions and recommendations with the UBC community. The reader should bear in mind that this is a student research project/report and is not an official document of UBC. Furthermore, readers should bear in mind that these reports may not reflect the current status of activities at UBC. We urge you to contact the research persons mentioned in a report or the SEEDS Sustainability Program representative about the current status of the subject matter of a project/report”. UBC NORTH CAMPUS SPIRAL DRAIN REPLACEMENT Final Design Report PREPARED FOR: Client Representative: Mr. Doug Doyle, P.Eng Associate Director, Infrastructure and Planning Client: UBC Social Ecological Economic Development Studies (SEEDS) Project Team 24: Rachel Jackson Danny Hsieh Mona Dahir Michael Louws Jasninder Gill Chris Vibe April 7th, 2017 Executive Summary Vortex Consulting has prepared a detailed design report, as requested by UBC Social, Ecological, Economic Development Studies (SEEDS), for the replacement of UBC's current North Campus Stormwater Management facility, the spiral drain. This report intends to provide UBC SEEDS with an understanding of the design components, technical analysis and design, and project costs and construction sequencing, that are required to mitigate a 1 in 200 year storm event.
    [Show full text]
  • Drop Structures
    DROP STRUCTURES 1 DESCRIPTION OF TECHNIQUE Drop structures (also known as grade controls, sills, or weirs) are low-elevation structures that span the entire width of the channel, creating an abrupt drop in channel bed and water surface elevation in a downstream direction. Drop structures have been used extensively in Washington State to stabilize channel grades, improve fish passage, and to reduce erosion. Generally speaking, in fish bearing waters, vertical drops must not exceed 1 foot [WAC 220-110-070]; lesser drops are often required to accommodate certain species and age classes of fish. Drop Structures are designed to spill and direct flow such that there is a distinct drop in water surface elevation at normal low flows. The purpose of drop structures may include but is not limited to: • redistribute or dissipate energy; • stabilize the channel bed; • restore a step pool morphology to an altered channel • limit channel incision; • limit bank erosion by directing flow away from an eroding bank; • modify the channel bed profile and form by promoting collection, sorting and deposition of sediment; • create structural and hydraulic diversity in uniform channels; • improve fish passage over natural and artificial barriers by backwatering the upstream reach; • scour the channel bed, creating holding pools for fish and other aquatic life; • provide backwater (depth) in groundwater fed side channels; or • raise the bed of an incised stream to reconnect it with its floodplain. Drop structures may resemble porous weirs in appearance. But while drop structures direct water over the structure and are applied primarily to modify the profile of a channel, porous weirs allow water to flow through the structure and are applied primarily to redirect or concentrate flow.
    [Show full text]
  • Drainage Design Manual
    THE CITY OF SAN DIEGO Transportation & Storm Water Design Manuals Drainage Design Manual January 2017 Edition The City of San Diego | Drainage Design Manual | January 2017 Edition DRAINAGE DESIGN MANUAL THIS PAGE INTENTIONALLY LEFT BLANK FOR DOUBLE-SIDED PRINTING The City of San Diego | Drainage Design Manual | January 2017 Edition CONTENT Contents Contents ............................................................................................................................................................... i Figures ............................................................................................................................................................... vii Tables .................................................................................................................................................................. ix Equations ............................................................................................................................................................. x 1. Introduction.............................................................................................................................................. 1-1 Policies ............................................................................................................................................... 1-1 Basic Objectives ......................................................................................................................... 1-2 Exceptions to Design Standards .............................................................................................
    [Show full text]
  • Whitewater Park Toolkit
    WHITEWATER PARK TOOLKIT A Paddler’s Guide to Championing a Local Project Every Project Needs a Local Champion Nationally, there are more than 1,000 rivers suitable for whitewater paddling, most of which are located off the beaten path and away from municipalities. Countless more, however, flow right through the heart of communities large and small. While many of these are not currently prone to paddling, with a little help they can be converted into destination whitewater play parks, becoming gathering places for their communities, enhancing the riparian zones, and even generating revenues for their towns. But it takes a champion and a little elbow grease. Most of today’s in-stream whitewater parks were the result of a paddler or group of paddlers that had a vision for a local park and the passion to get the ball rolling. Championing the development of a whitewater park for your community is not a simple process, nor is it the same from one community to the next. It takes tenacity, flexibility, and patience. Yet, armed with the right information and inspiration, you can be the spark that leads to a successful whitewater park in your community. The purpose of this Whitewater Park Toolkit is to serve as a guide for whitewater enthusiasts, anglers, and other community stakeholders to advocate for the development of a local in-stream whitewater park in their community. It provides a general understanding of the process, player, and costs involved in building a fun, safe, and environmentally S2O Design Whitewater Park Toolkit 01 CONTENTS 03
    [Show full text]
  • Site Visit and Conceptual Design Study Asheville Whitewater Park Asheville , N.C
    Site Visit and Conceptual Design Study Asheville Whitewater Park Asheville , N.C. February 19, 2015 Prepared for: Ben Van Camp Asheville Parks and Greenway Foundation P.O. Box 2362 Asheville, NC, 28802 Prepared by: Scott Shipley, P.E. S2o Design and Engineering 318 McConnell Drive Lyons, CO, 80540 1 318 McConnell Drive | Lyons, CO | 80540 Contents Introduction: ................................................................................................................................................. 4 Section 1: Whitewater Parks ......................................................................................................................... 5 Whitewater Parks Defined ........................................................................................................................ 5 The Whitewater Design Process ............................................................................................................... 7 Design Factors for Whitewater Facilities: ................................................................................................. 8 Stability ................................................................................................................................................. 9 Costs .................................................................................................................................................... 10 Typical Economic Impacts of Whitewater Parks ..................................................................................... 10 Section 2: Site
    [Show full text]
  • Floodplain Development in an Engineered Setting
    EARTH SURFACE PROCESSES AND LANDFORMS Earth Surf. Process. Landforms 34, 291–304 (2009) Copyright © 2008 John Wiley & Sons, Ltd. Published online 9 December 2008 in Wiley InterScience (www.interscience.wiley.com) DOI: 10.1002/esp.1725 FloodplainJohnChichester,ESPEarthEARTHThe0197-93371096-9837Copyright20069999ESP1725Research Journal Wiley Surf.ScienceSurface SURFACE ArticleArticles ©Process. &UK of2006 Sons, Processes the PROCESSES JohnBritish Ltd.Landforms Wiley and Geomorphological Landforms AND & Sons, LANDFORMS Ltd. Research Group development in an engineered setting Floodplain development in an engineered setting Michael Bliss Singer1,2* and Rolf Aalto3,4 1 School of Geography and Geosciences, University of St Andrews, St Andrews, Fife, UK 2 Institute for Computational Earth System Science, University of California Santa Barbara, Santa Barbara, CA, USA 3 Department of Geography, Archaeology, and Earth Resources, University of Exeter, Exeter, UK 4 Department of Earth and Space Sciences, University of Washington, Seattle, WA, USA Received 25 February 2008; Revised 20 May 2008; Accepted 2 June 2008 * Correspondence to: Michael Bliss Singer, Institute for Computational Earth System Science, University of California Santa Barbara, Santa Barbara, CA, USA. E-mail: [email protected] ABSTRACT: Engineered flood bypasses, or simplified conveyance floodplains, are natural laboratories in which to observe floodplain development and therefore present an opportunity to assess delivery to and sedimentation within a specific class of floodplain. The effects of floods in the Sacramento River basin were investigated by analyzing hydrograph characteristics, estimating event-based sediment discharges and reach erosion/deposition through its bypass system and observing sedimentation patterns with field data. Sediment routing for a large, iconic flood suggests high rates of sedimentation in major bypasses, which is corroborated by data for one bypass area from sedimentation pads, floodplain cores and sediment removal reporting from a government agency.
    [Show full text]
  • Design Guidelines and Details
    CHAPTER IV DESIGN GUIDELINES AND DETAILS A. General In this chapter, general design guidelines are provided for various bank stabilization methodologies introduced in Chapter II. Selection criteria for any of these erosion control methods is outlined in Chapter III. Details for the stabilization and erosion control methods discussed in this chapter are found in Appendix A. WEST PITTMAN CREEK DOWNSTREAM OF DIAMONDHEAD DRIVE, PLANO, TEXAS B. Structural and Armor Methods 1. Concrete-Lined Channel. Concrete-lined channels are a common drainage feature of small, urban streams in North Central Texas, especially in areas where right-of-way for drainage purposes is minimal. In addition to flood flow capacity, concrete lined channels should be designed to maintain scour velocities (>2 fps) throughout the expected flow regime. Supercritical flow will not be allowed. Minimum bottom width shall be 10 feet. Channel intersections shall be at an angle not exceeding IV-1 15 degrees. The minimum radius of centerline curvature shall be three times the top width of the channel unless superelevation computations are submitted for review. Subsurface drainage should be provided to prevent scour under the slabs and relieve pressures behind protected slopes. Uplift forces on the slabs should be evaluated. Joint location and frequency should be carefully considered by the design engineer (USACE, 1991). A typical concrete lined channel section is shown in Plate 1 of Appendix A. The designer is also referred to the standard details of the community in which they are working. 2. Rock Riprap Revetment. Rock or stone can be an effective erosion control measure if properly designed.
    [Show full text]